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An Offi

cial Publication of SciBiolMed.Org

ISSN: Online 2230-8598

www.journalonweb.com/ijmedph

Vol 4 | Issue 3 | Jul-Sep 2014

www.ijmedph.org

SciBiolMed.Org - A non-profi t private organization dedicated to Research in the fi eld of Science, Biology and Medicine. It provides high quality, accurate and required information to enhance re-search and innovative concepts in scholarly publishing.

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Vol 4, Issue 3, Jul-Sep 2014

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CONTENTS

Lithium content in potable water, surface water, ground water, and mineral water on the territory of Republic of Macedonia “Know your CD4 campaign”: 6-year outcomes from a quality improvement initiative to promote earlier initiation of antiretroviral therapy in Tanzania

A study of utilization pattern, effi cacy and safety of drugs prescribed for opportunistic infections in Human Immunodefi ciency Virus infected patients

Neurological manifestations of HIV-AIDS at a tertiary care center in western Maharashtra

The impact of severity of hypertension on auditory brainstem responses

Knowledge about childhood bronchial asthma among primary health care personnel in eastern Saudi Arabia

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Vesna Kostik, Biljana Bauer1,

Zoran Kavrakovski2

Institute of Public Health,

1Department of Pharmacognosy,

Faculty of Pharmacy, 2Department

of instrumental methods, Faculty of Pharmacy, University of Ss Cyril and Methodius, Skopje, Republic of Macedonia

Address for the Correspondence:

Prof. Biljana Bauer, Faculty of Pharmacy, University of Ss Cyril and Methodius, Majka Tereza 47,

1000 Skopje, Republic of Macedonia. E-mail: biba@ff.ukim.edu.mk

Lithium content in potable water, surface

water, ground water, and mineral water

on the territory of Republic of Macedonia

The aim of this study was to determine lithium concentration in potable water, surface water, ground, and mineral water on the territory of the Republic of Macedonia. Water samples were collected from water bodies such as multiple public water supply systems located in 13 cities, wells boreholes located in 12 areas, lakes and rivers located in three different areas. Determination of lithium concentration in potable water, surface water was performed by the technique of inductively coupled plasma-mass spectrometry, while in ground water samples from wells boreholes and mineral waters with the technique of ion chromatography. The research shows that lithium concentration in potable water ranging from 0.1 to 5.2 μg/L; in surface water from 0.5 to 15.0 μg/L; ground water from wells boreholes from 16.0 to 49.1 μg/L and mineral water from 125.2 to 484.9 μg/L. Obtained values are in accordance with the relevant international values for the lithium content in water.

Key words: Ground water, inductively coupled plasma-mass spectrometry, ion

chromatography, lithium, mineral water, potable water, surface water

Original Article

INTRODUCTION

Lithium is one of the most important trace elements for the functioning of the human organism. Mainly in the human body is inserted through the food of plant origin (cereals, nuts, vegetables) and water. Surveys conducted by Weiner[1] for the lithium intake in our organism, show that the main part

of the lithium intake is inserted through cereals and vegetables 430 and 2900 μg/day, while through food from animal origin in our body are inserted insignifi cant concentration (2.5 μg/day).

As a result, of the importance that lithium has on the functioning of the human body, scientists[2]

found that recomm ended daily dietary intake of lithium (recommended dietary allowance) for adults with an average body mass of 70 kg is 1 mg/day, which is equivalent to 14.3 μg/kg body mass. The US Environmental Protection Agency established standards for daily intake of lithium which for an adult, weight of 70 kg ranging from 650 to 3100 μg.[3] This concentration of lithium could be provided

with food and water intake which contain adequate concentrations of lithium.

Lithium from food or water in the form of soluble salts in the body is being completely absorbed in the gastrointestinal tract (small intestinum) trough Na+ channels. Absorbed lithium almost equally is

being distributed in the body fl uids with little difference between the extra cellular and intracellular fl uid. Lithium excretion of the body is carried out through kidneys. According to Hager et al.,[4] after the

autopsy in men and women who do not have any hetero anamnesis data of prior therapy with lithium preparations, the presence of lithium was found in the following organs: Cerebellum, cerebrum, kidney, thyroid, pancreas, lungs, and bones. From the obtained results can be concluded that the distribution of lithium is greater in women’s organs than in men, except in the pancreas. During embryogenesis, the concentration of lithium in the internal organs reaches a maximum concentration in the fi rst trimester of gestation, with a gradual decline to the end of the pregnancy.[5]

Biochemical mechanism of action of lithium in the body is very complex and is correlated with the present enzymes, hormones, vitamins and some drugs/medications. Infl uence of the lithium taken as a remedy on people’s mental behavior is due to increasing activity of monoamine oxidase,

Abstract

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Website: www.ijmedph.org DOI: 10.4103/2230-8598.137700 Quick response code:

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Kostik, et al.: Lithium content in water from the territory of Republic of Macedonia

as well as increased transport of folic acid and vitamin B12 in L1210 cells.[6] Biological activity of lithium is due to the powerful

polarization feature which is a result of its small ionic radius. Lithium can replace sodium, potassium, magnesium and calcium ions from the enzymes cofactors.[5] According to Ohgami et al.[7] the

luck of lithium in the body leads to a change in people’s behavior and increased aggression.

Lithium as an element which in nature is found in soil, primary in the clay fraction,[8] potable water, surface water, mineral water, ground

water and marine waters as well.

Because the primary source of lithium in humans are water and food, the objective of our research was determination of lithium content in potable water, surface water, ground water from wells boreholes and mineral water on the territory of the Republic of Macedonia, since such data have not been available so far.

MATERIALS AND METHODS

Water sampling

The samples of potable water from public water supply systems were investigated, as well as surface water, ground water from wells boreholes and mineral water taken from the territory of the Republic of Macedonia [Figure 1].

Determination of the concentration of lithium was performed in 30 samples of potable water from multiple public water supply systems/network in the Republic of Macedonia (Skopje, Tetovo,

Ohrid, Sveti Nikole, Bitola, Prilep, Strumica, Shtip, Radovish, Kriva Palanka, Kavadarci, Gevgelija and Veles). Determination of lithium concentration in surface water was done on 15 samples taken from several measuring points from the Ohrid Lake, river Lepenec and river Vardar (Gevgelija). The ground water samples from wells boreholes, 35 in total were taken from the territory: Skopje, Kavadarci, Radovish, Kumanovo, Bitola, Sveti Nikole, Prilep, Strumica and Negotino.

The proportion of different water samples in which content of lithium was determined is shown in the following Figure 2.

Analytical methods for determination

Determination of the concentration of lithium in potable water and surface water was performed with the technique of inductively coupled plasma-mass spectrometry. The NexION® 350D ICP-MS features a dual-channel Universal Cell as well the ability to use Dynamic Reaction Cell™ technology, giving analysts the fl exibility to choose Kinetic Energy Discrimination (KED) and/ or the use of a scanning quadrupole in the Dynamic Reaction Cell. These capabilities make it the ideal solution for biomonitoring applications. The limit of detection of lithium with this instrument is 0.05 μg/L.

Concentration of lithium in the ground water from wells boreholes and surface water were performed with the technique of ion chromatography with conductivity detector which covers the concentration areas for this type of waters. The performance of this instrument is given in Table 1.

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RESULTS AND DISCUSSION

Purpose of our investigation is to determine the concentration of lithium in potable water, surface water, ground water from wells boreholes and mineral water on the territory of the Republic of Macedonia. The results of the tests are given in Tables 2-5. Regulations for the water quality in the Republic of Macedonia provide no lithium content data. Therefore, our results were compared with literature data. Lithium was found in all analyzed water samples from the territory of Republic of Macedonia. Its concentrations depended on the type of water sample, which was analyzed [Table 6]. The heterogeneity of the results in the general research with a high coeffi cient of variation values implied that differences in the location and period of sampling had a major infl uence on the lithium content.

Research shows that concentration of lithium in the potable water from public water supply systems in the Republic of Macedonia ranging from 0.11 to 5.20 μg/L [Table 2]. In some regions of the world,[7,9] in order to increase the daily intake of lithium in human

nutrition, lithium is added as a supplement in the potable water (tap water), with the fi nal concentration of lithium in water of 170 μg/L. Low lithium concentration in potable water from multiple public water supply systems from the network in the Republic of Macedonia points to the possibility for a beginning of the enrichment of Macedonian potable water with lithium.

Determination of the concentration of lithium was performed in 30 samples of potable water from multiple public water supply systems/ network in the Republic of Macedonia. By calculating the average values of the lithium concentration according to the location the follow hierarchical lithium concentration gradient is obtained Skopje 2.84 μg/L, Kavadarci 1.81 μg/L, Sveti Nikole 1.56 μg/L, Gevgelija 1.33 μg/L, Shtip 1.00 μg/L, Strumica 0.67 μg/L, Tetovo 0.49 μg/L,

Figure 2: Percentage of the types of water in which is determined the

concentration of lithium

Table 1: Instrumental condition for determination of lithium with IC

Guard column Analytical column Eluent Regenerant

CG 16 3 mm × 50 mm CS 16 3 mm × 250 mm 30 mM methanesulfonic acid 100 mM tetrabutyl ammonium hydroxide

IC = Ion chromatography

Table 2: Results of determination of lithium in public water supply systems in the republic of macedonia (μg/L)

Location Period Lithium

concentration

Ohrid/Gradishte May 2010 0.25 Ohrid/Hotel Metropol May 2010 0.11 Tetovo/City tap April 2010 0.30 Skopje/Hotel Continental April 2009 5.20 Tetovo/Periphery May 2010 0.40 Tetovo/Center May 2010 0.78 Sveti Nikole/City tap April 2009 1.56 Skopje/Butel April 2011 2.40 Skopje/Karposh April 2011 2.89 Bitola/Center restaurant April 2009 0.23 Strumica/Hotel Sirius April 2010 0.90 Skopje/Center September 2011 1.20 Skopje/Chair November 2011 1.98 Prilep/Center May 2010 0.23 Strumica/Hotel Sirius April 2009 0.54 Strumica/Barracks April 2010 0.67 Strumica/Market-place May 2011 0.56 Radovish/Restaurant April 2009 0.43 Radovish/Household April 2010 0.48 Shtip/Restaurant at cultural

home Aco Shopov

April 2010 0.89 Shtip/Periphery (entry) April 2010 1.12 Kriva Palanka/Center April 2009 0.35 Veles/Intercity bus station April 2009 0.15 Kriva Palanka/Center May 2010 0.22 Skopje/Center April 2010 2.56 Skopje/Gjorche Petrov April 2010 3.65 Kavadarci/Center Restaurant April 2010 1.78 Gevgelija/Center Restaurant April 2009 1.12 Kavadarci/Center April 2010 1.85 Gevgelija/Center May 2010 1.55

Radovish 0.45 μg/L, Kriva Palanka 0.28 μg/L, Bitola 0.23 μg/L, Prilep 0.23 μg/L, Ohrid 0.18 μg/L and Veles 0.15 μg/L. If the territory of Republic of Macedonia is separated with river Vardar on the west and east part the estimated lithium concentrations of potable water are little bit higher in the east part (1.69 μg/L >1.34 μg/L).

Lithium concentration in surface water of 15 samples taken from several measuring points from the Ohrid Lake, river Lepenec and river Vardar (Gevgelija) are presented in Table 3. Lithium concentrations in surface water varied from 0.53 to 15.03 μg/L. Highest average lithium concentration was obtained on the measuring points at river Vardar near Gevgelija of 13.09 μg/L and the lowest average lithium concentration of 1.07 μg/L was obtained in the measuring points at Ohrid Lake.

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Kostik, et al.: Lithium content in water from the territory of Republic of Macedonia

Lithium composition of 35 in total ground water samples from wells boreholes, are presented in Tables 4 and 5. Twenty samples of ground water are categorized as mineral water, the rest 15 as potable

water according to our regulation limit.[10] Lithium levels were very

consistent at about 125.20-484.90 μg/L in mineral ground water. By calculating the average values of the lithium concentration according to the location of mineral ground water the follow hierarchical lithium concentration gradient is obtained Bitola 436.47 μg/L, Strumica 232.0 μg/L, Vizbegovo 170.18 μg/L, Kozuf 164.15 μg/L, Katlanovo 147.63 μg/L and Kumanovo 143.87 μg/L. The estimated lithium concentrations of mineral ground water are higher in the west part of the territory of Republic of Macedonia (300.31 μg/L >173.59 μg/L).

The obtained results [Table 5] for potable ground water were somewhat lower from 16.05 to 49.10 μg/L. According to the location of mineral ground water the follow hierarchical lithium concentration gradient is obtained Bitola 49.10 μg/L, Kumanovo 41.96 μg/L, Kavadarci, 33.44 μg/L, Petrovec 27.25 μg/L, Prilep

Table 6: Statistical processing of the results of determination of lithium in potable water, surface water, ground water and mineral water on the territory of republic of macedonia

Type of sample Lithium concentration

Public water supply systems

Average 1.21 CV 97.63 Surface water

Average 6.98 CV 72.61 Ground mineral water from wells

Average 224.78 CV 51.02 Ground water from wells

Average 26.73 CV 37.69

CV = Coeffi cient of variation

Table 4: Results of determination of lithium in ground mineral water from wells in the Republic of Macedonia, categorized as mineral water (μg/L)

Location Time Lithium

concentration

Vizbegovo well 1 April 2009 176.1 Vizbegovo well 2 April 2010 145.8 Vizbegovo well 3 May 2010 135.7 Kumanovo well 1 April 2009 155.8 Bansko, Strumica well 1 April 2009 210.9 Bansko, Strumica well 2 April 2009 256.5 Kumanovo well 1 May 2010 125.2 Medzitlija, Bitola well 1 April 2009 440.3 Medzitlija, Bitola well 2 April 2009 390.3 Kozuf well 1 April 2009 167.5 Medzitlija, Bitola well 1 May 2011 430.4 Medzitlija, Bitola well 2 May 2011 484.9 Bansko, Strumica well 1 May 2011 228.6 Kumanovo well 1 May 2011 150.6 Katlanovo well 1 April 2009 155.3 Katlanovo well 1 April 2010 148.9 Katlanovo well 1 April 2011 138.7 Kozuf well 1 May 2011 160.8 Vizbegovo well 1 September 2011 172.0 Vizbegovo well 4 September 2011 221.3

Table 3: Results of determination of lithium in surface water in the republic of macedonia (μg/L)

Location Time Lithium

concentration

Ohrid Sveti Naum September 2009 0.53 Ohrid Gradishte September 2009 0.78 Ohrid Gradska Plaza September 2009 2.30 Ohrid, Peshtani September 2009 0.78 River Lepenec, Zlokukani April 2009 5.53 River Lepenc, Gjorche Petrov,

before entry into Vardar

April 2009 7.77 River Lepenc, Gjorche Petrov,

entry into Vardar

April 2009 8.45 River Lepenc, Gjorche Petrov,

after entry into Vardar

April 2009 9.56 River Lepenec, Zlokukani May 2010 6.43 River Lepenc, Gjorche Petrov,

entry into Vardar

May 2010 9.24 River Vardar Gevgelija measuring

point 1 before the entrance to the bridge toward Bogorodica

April 2009 12.34 Ohrid Lagadin September 2009 0.95 River Vardar Gevgelija

measuring point 2 exit to the bridge toward Bogorodica

April 2009 10.12 River Vardar Gevgelija

measuring point 1

May 2010 15.03 River Vardar Gevgelija

measuring point 2

May 2010 14.89

Table 5: Results of determination of the li in ground water from wells in the republic of macedonia, categorized as potable water (μg/L)

Location Time Lithium

concentration

Sveti Nikole well 1 April 2009 17.56 Sveti Nikole well 2 April 2009 17.28 Prilep well 1 April 2009 23.50 Prilep well 2 April 2009 28.98 Radovish well 1 Maj 2009 19.40 Radovish well 2 Maj 2009 21.20 Radovish well 1 September 2010 16.05 Petrovec well 1 April 2009 34.40 Petrovec well 2 April 2010 24.80 Petrovec well 2 September 2011 22.56 Rosoman, Kavadarci well 1 April 2011 27.98 Rosoman, Kavadarci well 2 April 2011 38.90 Kumanovo well 1 April 2009 41.60 Negotino well 1 April 2009 17.65 Bitola well 1 September 2009 49.10

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26.24 μg/L, Radovish 18.88 μg/L, Negotino 17.65 μg/L and Sveti Nikole 143.87 μg/L. The estimated lithium concentrations of potable ground water are higher in the west part of the territory of Republic of Macedonia (31.61 μg/L >26.38 μg/L).

Research shows that concentration of lithium in the potable water, surface water, water from wells boreholes and mineral water from the territory of Republic of Macedonia is in accordance with the relevant international values for the content of lithium in water.[7,11]

CONCLUSION

If the estimated lithium concentrations values from the east and west part from the territory of Republic of Macedonia were compared could be noticed that more lithium was found in the west part. Macedonian potable water can serve as bad source of lithium able to supplement recommended daily dietary intake of lithium in the diet.

REFERENCES

1. Weiner ML. Overview in lithium tox icology. In: Sc hrauzer GN, Klippel KF, editors. Lithium in Biology and Medicine. Weinheim: VCG Verlag; 1991. p. 83-99.

2. Hager ED, Dziambor H, Winkler P, Macholdt K: Effekt von Lithium carbonat bei Patienten mit niedriger Thrombozytenzahl nach einer. In: Anke M,

How to cite this article: Kostik V, Bauer B, Kavrakovski Z. Lithium

content in potable water, surface water, ground water, and mineral water on the territory of Republic of Macedonia. Int J Med Public Health 2014;4:189-93.

Source of Support: Nil, Confl ict of Interest: None declared.

Arnhold W, Bergmann H. Proceedings Mengen und Spurenelemente, 20. Jahrestagung. Leipzig: Schubert - Verlag, 2000. p. 119-29.

3. Lu FC, Kacew S. Lu’s Basic Toxicology: Fundamentals, Target Organs and Risk Assessment. 4th ed. London: Taylor & Francis; 2003.

4. Hager ED, Dziambor H, Winkler P, Höhmann D, Macholdt K. Effects of lithium carbonate on hematopoietic cells in patients with persistent neutropenia following chemotherapy or radiotherapy. J Trace Elem Med Biol 2002;16:91-7. 5. Vanyo L, Vu T, Ramos M, Amin J, Conners S, Baterman R, et al. Lithium

induced perturbations of vitamin B12, folic acid and DNA metabolites. In: Schrauzer GN, Klippel KF, editors. Lithium in Biology and Medicine. Weinheim: VCG Verlag; 1991. p. 17-30.

6. Klemfuss H, Greene KE. Cation affecting lithium toxicity and pharmacology. In: Schrauzer GN, Klippel KF, editors. Lithium in Biology and Medicine. Weinheim: VCG Verlag; 1991. p. 133-45.

7. Ohgami H, Terao T, Shiotsuki I, Ishii N, I wata N. Lithium levels in drinking water and risk of suicide. Br J Psychiatry 2009;194:464-5.

8. Roberts FI. Mineralization of the Woolgangie-Yilma Area, Eastern Goldfi eld Granite Greenstone Terrain. Geological Survey Western Australia. Record; 2004. p. 6.

9. Anke M, Arnhold B, Glei M, Müller M, Illing H, Sch afer U, et al. Essentiality and toxicity of lithium. In: Kosla T, editor. Lithium in the Tropic-Chain-Soil-Plant-Animal-Man, Proceedings of International Symposium; 1998. Warshaw, Poland; 1998. p. 17-42.

10. Regulation for water safety, Sluzben Vesnik na Republika Makedonija, 46/08. 11. Schrauzer GN. Lithium: occurrence, dietary intakes, nutritional

References

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